1. Introduction
Simms Creek is a small, 3rd order stream that drains an area of
~1,800 ha into the Salish Sea, near Campbell River’s Willow Point
neighborhood. The lower reach of Simms Creek (~3 km of channel, east of
Dogwood Street), is contained within a narrow urban green way that is
bordered by residential properties. From Dogwood Street Road the streams
runs for ~ 2 km to the Inland Highway and is protected within Beaver
Lodge Lands , upstream of the Inland Highway, >1.5 km of tributary
channel is located within private forest lands in various stages of
regeneration.
Chum, Chinook, Pink and Coho salmon have all been observed in Simms
Creek, as well as Coastal Cutthroat Trout (CCT), Rainbow Trout and
steelhead. More recent monitoring (i.e., this dataset), suggest that
Coho Salmon (CO) and CCT are the primary species within Simms Creek,
both of which are present within the stream year round - though a small
number of juvenile Chinook Salmon were identified in 2024.
Greenways Land Trust has
supported Simms Creek Stewards for +20 years, including operation of a
fish fence near the mouth of the stream since 2008. Juvenile and adult
fish moving past the fence are tallied each spring and fall,
respectively. The objective of this project is to explore the juvenile
fence dataset. All work is being done strictly for fun and out of
personal curiosity. Any feedback, input, or support is welcome. Also, I
have a soft spot for CCT, so be warned that effort and results will be
slightly trout biased. Let’s take a look at what has been completed to
date. It’s a tremendous amount of work and all volunteers and supporters
should be commended!
Download Fence Data (.csv)
Download Enviromental Data (.csv)
2. Fence Operation
2.1. Monitoring Effort
The Simms Creek fish fence has operated annually since 2008, with the
exception of 2020 and 2021 when operations were paused due to the
COVID-19 Pandemic and in the spring of 2023 when federal employees were
on strike.
Spring surveys target out migrating juvenile Coho Salmon but also
capture an impressive number of CCT and have even captured some Chinook
Salmon. Spring fence monitoring has started as early as April 03,
however, most surveys (50%) don’t start until April 18. In each
monitoring year, the fence has operated continuously (e.g., sampling
occurred at least daily) from April 28 to May 30. Surveys have continued
as late as June 13, but most (50%) are terminated by June 06.
Fall surveys to count the number returning adult Coho, Chinook, Chum
and Pink Salmon and also intercept a small number of CCT. In the fall,
surveys have started as early as September 26, however, most surveys
(50%) have started on October 08. In each monitoring year, surveys have
occurred continuously (e.g., sampling occurred daily) from October 23 to
November 16. Surveys have continued as late as December 10 and no
surveys have occurred later than December 02.
Monitoring Effort Tables and Figures
Table 1. Sampling Summary
Table 2. Annual Spring and Fall Trap Operation Periods
Table 2. Annual spring and fall trap operation periods.
Spring Sampling
Fall Sampling
Year
# Days Sampled
Start
End
# Days Sampled
Start
End
2008
41
Apr-21
May-31
40
Oct-14
Nov-22
2009
50
Apr-19
Jun-07
40
Oct-14
Nov-22
2010
42
Apr-19
May-30
35
Oct-23
Nov-26
2011
49
Apr-19
Jun-06
46
Oct-18
Dec-02
2012
50
Apr-16
Jun-04
50
Oct-14
Dec-02
2013
49
Apr-14
Jun-01
62
Sep-29
Dec-01
2014
45
Apr-24
Jun-07
58
Oct-04
Nov-30
2015
52
Apr-10
May-31
62
Oct-08
Dec-08
2016
63
Apr-03
Jun-04
60
Oct-07
Dec-05
2017
68
Apr-05
Jun-11
56
Oct-11
Dec-05
2018
52
Apr-21
Jun-11
58
Oct-08
Dec-04
2019
51
Apr-18
Jun-07
64
Oct-08
Dec-10
2020
0
COVID
-
0
-
-
2021
0
COVID
-
0
-
-
2022
47
Apr-28
Jun-13
37
Oct-11
Nov-16
2023
0
DFO Strike
-
45
Sep-26
Nov-17
2024
55
Apr-12
Jun-05
0
-
-
2.2 Stream Conditions
During each daily trap visit, volunteers record measures of water
temperature, pH, Total Suspended Sediment (TSS), dissolved oxygen, and
water level (stage). Mean annual measures of each parameter are
presented below for the spring and fall monitoring periods (Table 3 and
Table 4, Figure 2).
Stream Conditions Figures and Tables
Table 3. Spring Condition Table
Table 3. Stream conditions during spring trap operation.
Year
Spring Monitoring
Air Temp. (°C)
Water Temp. (°C)
pH .
DO (mg/L)
TDS (ppm)
Water Level (m)
Mean
SD
Mean
SD
Mean
SD
Mean
SD
Mean
SD
Mean
SD
2008
9.5
4.0
10.5
2.8
7.1
0.3
10.8
0.8
67.8
36.8
0.2
0.0
2009
11.8
3.0
10.3
2.4
7.1
0.2
10.3
0.8
136.4
26.2
0.3
0.0
2010
9.5
2.2
10.0
1.6
8.2
0.3
10.5
1.8
110.2
17.4
0.2
0.1
2011
9.8
2.3
9.8
2.1
6.7
0.3
9.1
1.0
95.5
11.7
0.2
0.0
2012
11.0
2.1
10.2
1.7
7.4
0.8
9.9
1.4
99.4
17.2
0.2
0.1
2013
10.3
2.9
10.1
2.0
7.9
0.3
11.5
0.9
100.6
14.9
0.2
0.1
2014
12.2
2.4
11.3
1.7
8.1
0.5
9.7
0.6
97.8
19.2
0.2
0.1
2015
10.5
3.4
11.0
2.5
8.1
0.2
9.4
0.8
106.7
22.2
0.2
0.4
2016
11.4
2.8
11.7
1.8
7.1
0.4
10.2
1.5
111.3
20.1
0.1
0.0
2017
9.6
3.0
10.2
2.3
8.2
0.4
10.9
2.2
77.8
25.6
0.3
0.1
2018
10.7
2.5
8.7
1.3
8.8
1.4
14.2
1.6
153.9
21.2
0.1
0.0
2019
11.2
2.7
11.9
2.3
8.0
0.2
8.6
0.7
129.0
25.7
0.1
0.1
2022
11.7
2.5
12.2
16.0
7.5
0.3
-
-
83.0
17.2
0.2
0.1
2023
-
-
-
-
-
-
-
-
-
-
-
-
2024
12.1
2.2
10.3
2.1
7.7
0.4
10.2
0.9
129.8
30.0
0.1
0.0
Table 4. Fall Condition Table
Table 4. Stream conditions during fall trap operation.
Year
Fall Monitoring
Air Temp. (°C)
Water Temp. (°C)
pH .
DO (mg/L)
TDS (ppm)
Water Level (m)
Mean
SD
Mean
SD
Mean
SD
Mean
SD
Mean
SD
Mean
SD
2008
6.3
3.0
8.8
1.3
7.3
0.4
10.5
0.4
120.2
30.9
0.4
0.1
2009
6.8
3.3
8.7
1.9
7.6
0.2
10.6
1.9
105.0
28.7
0.5
0.2
2010
4.9
4.7
7.9
2.7
7.0
0.2
9.5
0.9
110.9
31.1
0.6
0.9
2011
4.9
3.0
7.0
1.8
7.3
0.6
9.7
0.5
112.7
30.1
0.3
0.3
2012
5.9
3.2
7.8
1.7
7.5
0.2
10.8
1.6
116.1
29.6
0.4
0.2
2013
6.1
3.1
8.0
2.0
7.7
0.1
10.5
0.7
119.8
30.6
0.3
0.1
2014
7.3
5.0
9.6
3.2
7.9
0.2
10.0
1.2
85.3
29.8
0.3
0.1
2015
6.0
4.3
8.5
3.0
8.2
0.2
10.2
2.1
97.1
29.5
0.3
0.2
2016
7.8
3.1
9.3
1.8
8.1
1.3
9.3
1.3
54.0
9.2
0.5
0.2
2017
4.8
3.3
8.4
1.9
8.1
0.7
12.8
1.4
101.8
38.2
0.3
0.2
2018
6.4
3.5
9.2
1.9
7.9
0.3
10.4
0.6
88.8
29.0
0.3
0.1
2019
5.2
3.8
8.2
2.3
7.6
0.1
11.5
1.0
103.9
26.6
0.2
0.1
2022
6.9
4.9
8.4
2.5
7.8
0.2
10.1
-
126.9
83.3
0.2
0.6
2023
8.3
5.4
9.6
2.4
7.8
0.2
10.7
0.7
66.4
66.1
0.2
0.1
2024
-
-
-
-
-
-
-
-
-
-
-
-
2.3. Annual Captures
Since 2008, a total of 5,046 juvenile CCT and 8,216 juvenile Coho
Salmon have been captured during spring trapping. Annual captures of CCT
have ranged from 45 to 849 (mean = 360) while CO captures have varied
from 335 to 913 with an overall mean of 587 fish (Figure 3 and Figure 4,
Table 5 and Table 6).
As expected, most fish are captured in the Spring. Catches of CCT
have ranged from 45 to 849 during spring (mean = 360 \(\pm\) 276.5) compared to only 1 to 9 fish
during fall (mean = 2 \(\pm\) 2.8).
Annual Captures Figures and Tables
Table 5. Spring - Total annual catches
**Table 5. Spring capture summary - capture timing, total captures and length of CCT and Coho Salmon.**
CCT
Coho Salmon
Total
Sample Period
Capture Timing
Fork Length (mm)
Capture Timing
Fork Length (mm)
(CT+CO)
Year
Start
End
# Days Sampled
Med.
Min
Max
n
Mean
SD
Min
Max
Med.
Min
Max
n
Mean
SD
Min
Max
n
2008
Apr-21
May-31
41
May-20
Apr-21
May-31
756
139.1
27.6
90
280
May-17
Apr-25
May-31
512
118.1
10.7
84.0
150
1268
2009
Apr-19
Jun-07
50
May-16
Apr-20
Jun-03
225
163.3
22.9
115
265
May-20
Apr-24
Jun-07
658
100.2
11.0
11.0
160
883
2010
Apr-19
May-30
42
May-13
Apr-19
May-29
502
149.7
26.1
110
285
May-13
Apr-20
May-30
477
118.0
15.7
80.0
183
979
2011
Apr-19
Jun-06
49
May-15
Apr-23
Jun-05
624
155.3
32.5
95
400
May-17
Apr-20
Jun-06
602
113.1
12.8
80.0
147
1226
2012
Apr-16
Jun-04
50
May-08
Apr-23
Jun-01
465
160.1
33.7
80
335
May-13
Apr-16
Jun-04
689
107.8
12.4
75.0
145
1154
2013
Apr-14
Jun-01
49
May-09
Apr-16
May-30
461
161.4
26.5
95
350
May-12
Apr-15
Jun-01
913
106.7
9.9
83.0
150
1374
2014
Apr-24
Jun-07
45
May-09
Apr-27
Jun-02
76
142.1
29.2
70
310
May-12
Apr-26
Jun-05
376
103.2
12.4
80.0
223
452
2015
Apr-10
May-31
52
May-09
Apr-15
May-28
141
158.1
37.4
85
260
May-13
Apr-11
May-31
761
109.3
11.7
78.0
152
902
2016
Apr-03
Jun-04
63
Apr-26
Apr-05
May-15
77
147.5
37.4
88
250
May-05
Apr-05
Jun-04
817
108.0
13.4
0.0
162
894
2017
Apr-05
Jun-11
68
May-24
Apr-20
Jun-09
65
185.1
64.0
120
470
May-20
Apr-05
Jun-11
335
113.4
12.8
80.0
162
400
2018
Apr-21
Jun-11
52
May-04
Apr-26
May-27
45
167.4
28.2
120
230
May-19
Apr-21
Jun-11
647
101.4
11.1
9.0
170
692
2019
Apr-18
Jun-07
51
May-06
Apr-18
May-30
571
146.1
27.6
95
260
May-13
Apr-24
Jun-05
405
115.4
12.9
10.7
152
976
2022
Apr-28
Jun-13
47
May-19
Apr-29
Jun-13
189
168.5
33.6
98
430
May-21
Apr-28
Jun-10
366
113.7
13.0
80.0
170
555
2024
Apr-12
Jun-05
55
Apr-29
Apr-17
Jun-03
849
159.8
37.1
50
360
May-10
Apr-18
Jun-04
658
97.5
17.6
48.0
174
1507
Table 6. Fall - Total annual catches
**Table 6. Fall capture summary - capture timing, total captures and length of CCT and Coho Salmon.**
CCT
Coho Salmon
Sample Period
Capture Timing
Fork Length (mm)
Capture Timing
Fork Length (mm)
Year
Start
End
# Days Sampled
Med.
Min
Max
n
Mean
SD
Min
Max
Med.
Min
Max
n
Mean
SD
Min
Max
2008
Oct-14
Nov-22
40
Nov-03
Nov-03
Nov-03
1
440.0
-
440
440
Nov-02
Oct-31
Nov-03
5
638.0
78.9
540
720
2009
Oct-14
Nov-22
40
-
-
-
0
-
-
-
-
Nov-03
Oct-17
Nov-18
12
648.3
84.1
490
790
2010
Oct-23
Nov-26
35
Nov-11
Nov-11
Nov-11
1
290.0
-
290
290
Oct-25
Oct-24
Nov-22
37
640.1
91.5
405
780
2011
Oct-18
Dec-02
46
-
-
-
0
-
-
-
-
Nov-12
Oct-26
Nov-23
30
650.5
82.9
370
795
2012
Oct-14
Dec-02
50
Oct-28
Oct-28
Oct-28
1
580.0
-
580
580
Nov-01
Oct-14
Nov-20
17
583.2
107.1
300
690
2013
Sep-29
Dec-01
62
-
-
-
0
-
-
-
-
Nov-06
Nov-02
Nov-18
83
631.7
59.7
490
790
2014
Oct-04
Nov-30
58
Oct-28
Oct-28
Oct-28
1
430.0
-
430
430
Oct-28
Oct-15
Nov-27
91
627.8
87.8
330
830
2015
Oct-08
Dec-08
62
-
-
-
0
-
-
-
-
Nov-08
Oct-12
Dec-02
77
600.0
89.4
350
750
2016
Oct-07
Dec-05
60
-
-
-
0
-
-
-
-
Nov-01
Oct-24
Nov-17
9
632.8
77.9
510
750
2017
Oct-11
Dec-05
56
Nov-19
Nov-19
Nov-19
1
470.0
-
470
470
Nov-15
Oct-18
Dec-04
19
592.4
133.3
330
770
2018
Oct-08
Dec-04
58
Nov-01
Nov-01
Nov-01
1
330.0
-
330
330
Nov-14
Oct-26
Nov-28
25
605.5
91.0
380
790
2019
Oct-08
Dec-10
64
Oct-16
Oct-16
Oct-16
1
390.0
-
390
390
Oct-25
Oct-16
Nov-17
22
566.8
110.2
340
710
2022
Oct-11
Nov-16
37
-
-
-
0
-
-
-
-
Nov-03
Oct-24
Nov-06
125
612.7
97.5
220
750
2023
Sep-26
Nov-17
45
Nov-02
Nov-02
Nov-16
9
239.1
108.9
152
430
Oct-18
Oct-11
Nov-16
272
571.3
96.5
220
740
2.4 Length Frequency
The length frequency figures shown below shed light on the population
structure and behaviours of Coho Salmon and CCT in Simms Creek. The
lengths of CCT (50 mm to 223 mm) and Coho Salmon (48 mm to 223 mm)
measured at the fence suggest multiple age classes of juveniles are
moving out of the system each spring. Assuming that CO <100 mm are
Age 0 and CO >100 mm are Age 1 would suggest that 55.20% of all
overall migrants are Age 0 and the remainder are Age 1. A wider range of
age classes is likely present among CCT, including Age 0 fish (~<80
mm) up to mature fish > 230 mm and upwards of 3+ years.
Mature CCT >230 mm represent <1.90% of the total catch of CCT.
However, all mature CCT >230 mm were moving downstream, suggesting
that they either 1) moved upstream and spawned prior to the start of
fence operation or 2) had overwintered in Simms Creek and were follow
fry out in the spring - whether this was their first movement to the
ocean is unknown.
Length Frequency Table and Figures
2.5 Age Composition
No scale data has been collected during juvenile enumeration work on
Simms Creek. However, information collected on systems within the region
suggests we can loosely apply the following age classes to juvenile CT
and CO:
CT < 80 ~ Age-0
CT < 120 ~ Age-1
CT < 200 ~ Age-2
CT > 200 ~ Age-2+
CO < 80 ~ Age-0
CO < 120 ~ Age-1
CO > 120 ~ Age-1+
Applying these age bins to the length frequency data suggests that
CCT are range in age from Age-1 to Age 3+, but are primarily Age-2
(Figure 9), while CO are almost exclusively Age-1 (Figure 10).
Interestingly, Age-0 CO were present in 2009 and 2024, but not other
years. While this may be coincidental, it’s worth noting that the peak
juvenile CCT counts were recorded in 2008 and 2024. There are a number
of mechanisms that may explain why Age-0 CO were first observed in 2024:
1) they weren’t recorded in past years, CO emigrated out of Simms Creek
earlier than normal due to high CT abundance.
Figure 10. Size by age class across years.
2.6. Migration Timing
2.4.1 Spring Outmigration
Outmigrating juvenile CCT and Coho Salmon were first encountered at
the trap over a similar period, from October 16 to November 19 (mean
\(\pm\) SD = November 01 \(\pm\) 10.1 days) for CCT and October 11 to
November 02 for Coho (mean \(\pm\) SD =
October 20 \(\pm\) 7 days). On average
50% of all CCT had passed the fence by November 02\(\pm\) 10.1 days while half of Coho Salmon
migrants had passed the fence by November 05\(\pm\) 8 days. Despite similarities in when
migrations started and the timing that most migrants had past the fence,
there was a noticeable difference in the timing of peak migrations (the
date when the greatest number of fish passed the fence). For Coastal
CCT, the overall mean \(\pm\) SD peak
migration occurred on November 01(\(\pm\) 10.1 days) (Figure 5) whereas overall
mean peak Coho Salmon migration occurred more than a week later on
October 30 (\(\pm\) 11.4 days) (Figure
6). Total number of daily captures of CCT and Coho Salmon per year are
presented in Figure 6 and Figure 7, respectively.
2.4.2 Fall Return Timing
Adult Coho Salmon have been detected at the fence as early as October
11 and as late as November 02, though most of the run (50%) arrive
within a week of November 05 (Figure 14 to 19). Relative to spring
sampling, CCT are encountered less frequently in the fall and arrival
timing appears to be considerably more variable (Figure 20 to 22).
Spring and Fall Migration Timing Tables and Figures
2.6 What are these fish doing???
CCT show incredible diversity in the timing of their life history
behaviours. Throughout their range, spawning has been documented in
nearly every month of the year. In Puget Sound for instance, spawning
has been reported from November through March and timing is highly
variable between years (Losee
et al. 2016 ). The spawn timing of CCT in Simms Creek is unknown, or
at least undocumented, however, I would assume it occurs during a
similar period to Puget Sound and is equally variable.
The current dataset does provide some insight on spawn timing.
Presumably, spawners will be >150 mm in length.
---
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# 1. Introduction

Simms Creek is a small, 3rd order stream that drains an area of \~1,800 ha into the Salish Sea, near Campbell River's Willow Point neighborhood. The lower reach of Simms Creek (\~3 km of channel, east of Dogwood Street), is contained within a narrow urban green way that is bordered by residential properties. From Dogwood Street Road the streams runs for ~ 2 km to the Inland Highway and is protected within [Beaver Lodge Lands](https://campbellriver.travel/news/forestry-guide-to-beaver-lodge-lands/), upstream of the Inland Highway, \>1.5 km of tributary channel is located within private forest lands in various stages of regeneration.

Chum, Chinook, Pink and Coho salmon have all been observed in Simms Creek, as well as Coastal Cutthroat Trout (CCT), Rainbow Trout and steelhead. More recent monitoring (i.e., this dataset), suggest that Coho Salmon (CO) and CCT are the primary species within Simms Creek, both of which are present within the stream year round - though a small number of juvenile Chinook Salmon were identified in 2024.

[Greenways Land Trust](https://www.greenwaystrust.ca/) has supported Simms Creek Stewards for +20 years, including operation of a fish fence near the mouth of the stream since 2008. Juvenile and adult fish moving past the fence are tallied each spring and fall, respectively. The objective of this project is to explore the juvenile fence dataset. All work is being done strictly for fun and out of personal curiosity. Any feedback, input, or support is welcome. Also, I have a soft spot for CCT, so be warned that effort and results will be slightly trout biased. Let's take a look at what has been completed to date. It's a tremendous amount of work and all volunteers and supporters should be commended!



```{r 1. Load and Format Data, echo = FALSE, warning = FALSE, message = FALSE}
## Clear workspace ##
# rm(list = ls())  

# ## Load Prepped Data
# source("SourceFiles/0. RunSourceFiles.R")
# 
  source("SourceFiles/1. Load and Prep Data.R")
# 
# ## Load Trap Effort Data
 source("SourceFiles/2. Trapping Effort.R")

```

```{r download data}
data_all %>%
download_this(
    output_name = "Raw Fence Data",
    output_extension = ".csv",
    button_label = "Download Fence Data (.csv)",
    button_type = "default",
    has_icon = TRUE,
    icon = "fa fa-save"
  )

simms_env %>%
download_this(
    output_name = "Raw Fence Data",
    output_extension = ".csv",
    button_label = "Download Enviromental Data (.csv)",
    button_type = "default",
    has_icon = TRUE,
    icon = "fa fa-save"
  )
```


# 2. Fence Operation

### 2.1. Monitoring Effort {.tabset .tabset-dropdown}
The Simms Creek fish fence has operated annually since 2008, with the exception of 2020 and 2021 when operations were paused due to the COVID-19 Pandemic and in the spring of 2023 when federal employees were on strike.

Spring surveys target out migrating juvenile Coho Salmon but also capture an impressive number of CCT and have even captured some Chinook Salmon. Spring fence monitoring has started as early as `r format(min(trap_plot$date.std[trap_plot$Period=="Spring"]), "%B %d")`, however, most surveys (50%) don't start until `r format(min(trap_plot$date.std[trap_plot$Period=="Spring" & trap_plot$prop.sampled >= 0.5]), "%B %d")`. In each monitoring year, the fence has operated continuously (e.g., sampling occurred at least daily) from `r format(min(trap_plot$date.std[trap_plot$Period=="Spring" & trap_plot$prop.sampled == 1.0]), "%B %d")` to `r format(max(trap_plot$date.std[trap_plot$Period=="Spring" & trap_plot$prop.sampled == 1.0]), "%B %d")`. Surveys have continued as late as `r format(max(trap_plot$date.std[trap_plot$Period=="Spring"]), "%B %d")`, but most (50%) are terminated by `r format(max(trap_plot$date.std[trap_plot$Period=="Spring" & trap_plot$prop.sampled==0.5]), "%B %d")`.

Fall surveys to count the number returning adult Coho, Chinook, Chum and Pink Salmon and also intercept a small number of CCT. In the fall, surveys have started as early as `r format(min(trap_plot$date.std[trap_plot$Period=="Fall"]), "%B %d")`, however, most surveys (50%) have started on `r format(min(trap_plot$date.std[trap_plot$Period=="Fall" & trap_plot$prop.sampled >= 0.5]), "%B %d")`. In each monitoring year, surveys have occurred continuously (e.g., sampling occurred daily) from `r format(min(trap_plot$date.std[trap_plot$Period=="Fall" & trap_plot$prop.sampled == 1.0]), "%B %d")` to `r format(max(trap_plot$date.std[trap_plot$Period=="Fall" & trap_plot$prop.sampled == 1.0]), "%B %d")`. Surveys have continued as late as `r format(max(trap_plot$date.std[trap_plot$Period =="Fall"]), "%B %d")` and no surveys have occurred later than `r format(max(trap_plot$date.std[trap_plot$Period=="Fall" & trap_plot$prop.sampled >= 0.5]), "%B %d")`.


#### Monitoring Effort Tables and Figures

#### Table 1. Sampling Summary
```{r 2. Trap Effort Summary Table , fig.cap = "Table 1. Summary of spring and fall sampling effort.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE}

kable(trap_effort_summary_table,
      "html",
      booktabs = T,
      
      align = c("c"),
      col.names = c("Period","Min","Max", "Mean", "SD",
                             "Min","Max", "Mean", "SD",
                             "Min","Max", "Mean", "SD"),
      caption = "Table 1. Annual spring trap operation periods.",
      digits = 1) %>%
    
      kable_styling("striped", full_width =  FALSE,
                      position = "center", 
                      font_size = 12,
                      fixed_thead = TRUE) %>%
        add_header_above(c(" " = 1, "# Days Sampled" = 4, "Start Date" = 4, "End Date"=4))

```


#### Table 2. Annual Spring and Fall Trap Operation Periods
```{r 2. Trap Effort Table trap effort table, fig.cap = "Table 2. Annual spring and fall trap operation periods.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE}


## Kable - Master Summary ----
options(knitr.kable.NA = '-')
    

    kable(trap_effort_table,
      "html",
      booktabs = T,
      
      align = c("c"),
      col.names = c("Year", "# Days Sampled", "Start", "End", 
                            "# Days Sampled", "Start", "End"),
      caption = "Table 2. Annual spring and fall trap operation periods.",
      
      digits = 1) %>%
  column_spec(c(2,5), width = "2cm") %>%
  kable_styling("striped", full_width =  FALSE,
                position = "center", 
                font_size = 12,
                fixed_thead = TRUE) %>%
  add_header_above(c(" " = 1, "Spring Sampling" = 3, "Fall Sampling" = 3))
```


<!-- **`r fig_nums("fall.trap.plot", "Fall trap operation period, presented as the proportion of sample years each date has been trapped since 2008 (excluding years when trapping did not occur due to COVID or government strikes).")`** -->



```{r 3. Stream Conditions - Load Data, echo=FALSE, warning=FALSE, message = FALSE}

## Load Stream Conditions Data 
 source("SourceFiles/3. Stream Conditions.R")

```

### 2.2 Stream Conditions {.tabset .tabset-dropdown}

During each daily trap visit, volunteers record measures of water temperature, pH, Total Suspended Sediment (TSS), dissolved oxygen, and water level (stage). Mean annual measures of each parameter are presented below for the spring and fall monitoring periods (Table 3 and Table 4, Figure 2). 

#### Stream Conditions Figures and Tables

#### Table 3. Spring Condition Table
```{r 3. Stream Conditions - Spring Table, fig.cap = "Table 3. Overall annual stream conditions during spring trap monitoring from 2008 to 2024.", fig.topcaption = TRUE,echo=FALSE, warning=FALSE, message = FALSE}

cond_data_wide.spring <- cond_data_wide %>% select(1:13)

## Kable - Stream Conditions ----
options(knitr.kable.NA = '-')
    

    kable(cond_data_wide.spring,
      "html",
      booktabs = T,
      
      align = c("c"),
      col.names = c(" ", "Mean","SD","Mean","SD","Mean","SD","Mean","SD","Mean","SD","Mean","SD"),
      caption = "Table 3. Stream conditions during spring trap operation.",
      
      digits = 1) %>%
  column_spec(c(2,5), width = "2cm") %>%
  kable_styling("striped", full_width =  FALSE,
                position = "center", 
                font_size = 12,
                fixed_thead = TRUE) %>% 
  add_header_above(c(" " = 1, "Air Temp. \n(\u00B0C)" = 2, "Water Temp. \n(\u00B0C)" = 2, 
                              "pH \n. " = 2, "DO \n(mg/L)" = 2, "TDS \n(ppm)" = 2, "Water Level \n(m)" = 2)) %>%
  add_header_above(c("Year"= 1, "Spring Monitoring" = 12))    

```

#### Table 4. Fall Condition Table
```{r 3. Stream Conditions - Fall Table, fig.cap = "Table 4. Overall annual stream conditions during fall trap monitoring from 2008 to 2024.", fig.topcaption = TRUE,echo=FALSE, warning=FALSE, message = FALSE}

cond_data_wide.spring <- cond_data_wide %>% select(1, 14:25)

## Kable - Stream Conditions ----
options(knitr.kable.NA = '-')
    

    kable(cond_data_wide.spring,
      "html",
      booktabs = T,
      
      align = c("c"),
      col.names = c(" ", "Mean","SD","Mean","SD","Mean","SD","Mean","SD","Mean","SD","Mean","SD"),
      caption = "Table 4. Stream conditions during fall trap operation.",
      
      digits = 1) %>%
  column_spec(c(2,5), width = "2cm") %>%
  kable_styling("striped", full_width =  FALSE,
                position = "center", 
                font_size = 12,
                fixed_thead = TRUE) %>% 
  add_header_above(c(" " = 1, "Air Temp. \n(\u00B0C)" = 2, "Water Temp. \n(\u00B0C)" = 2, 
                              "pH \n. " = 2, "DO \n(mg/L)" = 2, "TDS \n(ppm)" = 2, "Water Level \n(m)" = 2)) %>%
  add_header_above(c("Year"= 1, "Fall Monitoring" = 12))    
```



#### Figure 2. Spring and Fall Condition Plot
```{r 3. Stream Conditions - Plot, fig.cap = "Figure 2. Average daily measures of air and water temperature, pH, dissolved oxygen (DO), total dissolved solids (TDS) and water level (stage) per monitoring year in spring and fall.", echo=FALSE, warning=FALSE, message = FALSE, fig.width = 10, fig.height = 15, fig.topcaption = TRUE}

print(cond_plot)
```

### 2.3. Annual Captures {.tabset .tabset-dropdown}
```{r 4. Fish Captures - Summary Table catch_dat.prep, echo=FALSE, warning=FALSE, message = FALSE, include = FALSE}
source("SourceFiles/4. Annual Captures.R")
```

```{r 4. Fish Captures - values for text, echo=FALSE, warning=FALSE, message = FALSE, include = FALSE}
annual.catches <- catch_plot.data %>% group_by(Period, Species) %>%
                                         summarize(mean = round(mean(n),0),
                                                   min = min(n),
                                                   max = max(n),
                                                   SD  = sd(n))
annual.catches.spring.CT <- annual.catches %>% filter(Period == "Spring", Species == "CT")
annual.catches.spring.CO <- annual.catches %>% filter(Period == "Spring", Species == "CO")
annual.catches.fall.CT <- annual.catches %>% filter(Period == "Fall", Species == "CT")
annual.catches.fall.CO <- annual.catches %>% filter(Period == "Fall", Species == "CO")
```



Since 2008, a total of `r format(sum(catch_annual.Table.Spring$nCT), big.mark =",")` juvenile CCT and `r format(sum(catch_annual.Table.Spring$nCO), big.mark =",")` juvenile Coho Salmon have been captured during spring trapping. Annual captures of CCT have ranged from `r format(min(catch_annual.Table.Spring$nCT), big.mark =",")` to `r format(max(catch_annual.Table.Spring$nCT), big.mark =",")` (mean = `r format(mean(catch_annual.Table.Spring$nCT), digits = 1)`) while CO captures have varied from `r format(min(catch_annual.Table.Spring$nCO), big.mark =",")` to `r format(max(catch_annual.Table.Spring$nCO), big.mark =",")` with an overall mean of `r format(mean(catch_annual.Table.Spring$nCO), digits = 1)` fish (Figure 3 and Figure 4, Table 5 and Table 6).

As expected, most fish are captured in the Spring. Catches of CCT have ranged from `r annual.catches.spring.CT$min` to `r annual.catches.spring.CT$max` during spring (mean = `r annual.catches.spring.CT$mean` $\pm$ `r round(annual.catches.spring.CT$SD,1)`) compared to only `r annual.catches.fall.CT$min` to `r annual.catches.fall.CT$max` fish during fall (mean = `r annual.catches.fall.CT$mean` $\pm$ `r round(annual.catches.fall.CT$SD,1)`). 


#### Annual Captures Figures and Tables

#### Figure 3. Spring - Total annual catches
```{r 4. Annual Captures - Spring Summary Plot, fig.cap = "Figure 3. Total annual catch of CCT and Coho Salmon during Spring fence monitoring.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 10, fig.height = 12}

print(catch_annual_barPlot.Spring)
```
#### Table 5. Spring - Total annual catches
```{r 4. Annual Captures - Spring Summary Table, echo=FALSE, warning=FALSE, message = FALSE}
## Kable - Master Summary ----
options(knitr.kable.NA = '-')

catch_annual.Table.Spring %>% group_by(Year) %>% mutate(total.catch = nCT + nCO)

kable(catch_annual.Table.Spring  %>% group_by(Year) %>% mutate(total.catch = nCT + nCO),
      "html",
      booktabs = T,
      
      align = c("c"),
      # col.names = c("Year", "Period", "Start", "End", "# Days Sampled", 
      col.names = c("Year", "Start", "End", "# Days Sampled",  
                    "Med.","Min","Max", "n", "Mean", "SD" ,"Min","Max",
                    "Med.","Min","Max", "n", "Mean", "SD" ,"Min","Max", "n"),
      caption = "**Table 5. Spring capture summary - capture timing, total captures and length of CCT and Coho Salmon.**",
      digits = 1) %>%
  #column_spec(c(1, 3,10,17), bold = TRUE) %>%
  kable_styling("striped", full_width =  FALSE,
                position = "center", 
                font_size = 12,
                fixed_thead = TRUE) %>%
  # add_header_above(c(" " = 2, "Sample Period" = 3, 
  add_header_above(c(" " = 1, "Sample Period" = 3,                   
                     "Capture Timing" = 3,"Fork Length (mm)" = 5,
                     "Capture Timing" = 3,"Fork Length (mm)" = 5,"(CT+CO)"=1)) %>%
  add_header_above(c(" " = 4, "CCT" = 8, "Coho Salmon" = 8,"Total"=1)) 
```

#### Figure 4. Fall - Total annual catches
```{r 4. Annual Captures - Fall Summary Plot, fig.cap = "Figure 4. Total annual catch of CCT and Coho Salmon during fall fence monitoring.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 10, fig.height = 12}

print(catch_annual_barPlot.Fall)
```

#### Table 6. Fall - Total annual catches
```{r Annual Captures - Fall Summary Table, echo=FALSE, warning=FALSE, message = FALSE}
## Kable - Master Summary ----
options(knitr.kable.NA = '-')

kable(catch_annual.Table.Fall,
      "html",
      booktabs = T,
      
      align = c("c"),
      # col.names = c("Year", "Period", "Start", "End", "# Days Sampled", 
      col.names = c("Year", "Start", "End", "# Days Sampled",  
                    "Med.","Min","Max", "n", "Mean", "SD" ,"Min","Max",
                    "Med.","Min","Max", "n", "Mean", "SD" ,"Min","Max"),
      caption = "**Table 6. Fall capture summary - capture timing, total captures and length of CCT and Coho Salmon.**",
      digits = 1) %>%
  #column_spec(c(1, 3,10,17), bold = TRUE) %>%
  kable_styling("striped", full_width =  FALSE,
                position = "center", 
                font_size = 12,
                fixed_thead = TRUE) %>%
  # add_header_above(c(" " = 2, "Sample Period" = 3, 
  add_header_above(c(" " = 1, "Sample Period" = 3,                   
                     "Capture Timing" = 3,"Fork Length (mm)" = 5,
                     "Capture Timing" = 3,"Fork Length (mm)" = 5)) %>%
  add_header_above(c(" " = 4, "CCT" = 8, "Coho Salmon" = 8)) 
```
### 2.4 Length Frequency {.tabset .tabset-dropdown}
```{r 6. Length Frequency - Load Data, echo=FALSE, warning=FALSE, message = FALSE, include = FALSE}
 source("SourceFiles/6. Length Frequency.R")
```

```{r 6. length values, echo = FALSE, warning = FALSE, message = FALSE, include = FALSE}
spring.dat <- data_all %>% filter(Period == "Spring",
                                  Length>20,
                                  Species %in% c("CO","CT"))
CO_min <- min(spring.dat$Length[spring.dat$Species=="CO"], na.rm = TRUE)
CO_max <- max(spring.dat$Length[spring.dat$Species=="CO"], na.rm = TRUE)


CT_min <- min(spring.dat$Length[spring.dat$Species=="CT"], na.rm = TRUE)
CT_max <- max(spring.dat$Length[spring.dat$Species=="CT"], na.rm = TRUE)

Aged <- spring.dat %>% mutate(Age =ifelse(Species == "CO",
                                          ifelse(Length <110, 0, 1),
                                    ifelse(Species == "CT", 
                                         ifelse(Length <80, 0,
                                               ifelse(Length <150, 1, 2)),NA))) %>%
                        select(Period, Species, Length, Age)

                          
    age.table <- Aged %>% mutate(Age = as.factor(Age)) %>%
                          group_by(Species, Age) %>%
                          summarise(n = n(),
                                    min = min(Length),
                                    max = max(Length),
                                    avg = mean(Length))
    
CO.Age0.perc <- age.table$n[age.table$Species =="CO" & 
                            age.table$Age ==0]/(age.table$n[age.table$Species =="CO" & 
                                                           age.table$Age ==0]+ 
                                                  age.table$n[age.table$Species =="CO" & 
                                                            age.table$Age ==1])
                                                                       
```


The length frequency figures shown below shed light on the population structure and behaviours of Coho Salmon and CCT in Simms Creek. The lengths of CCT (`r CT_min` mm to `r CO_max` mm) and Coho Salmon (`r CO_min` mm to `r CO_max` mm) measured at the fence suggest multiple age classes of juveniles are moving out of the system each spring. Assuming that CO <100 mm are Age 0 and CO >100 mm are Age 1 would suggest that `r percent(round(CO.Age0.perc,digits = 3))` of all overall migrants are Age 0 and the remainder are Age 1. A wider range of age classes is likely present among CCT, including Age 0 fish (~<80 mm) up to mature fish > 230 mm and upwards of 3+ years. 

Mature CCT >230 mm represent <`r percent(round(CT.AgeClass.Prop$Adult, digits =3))` of the total catch of CCT. However, all mature CCT >230 mm were moving downstream, suggesting that they either 1) moved upstream and spawned prior to the start of fence operation or 2) had overwintered in Simms Creek and were follow fry out in the spring - whether this was their first movement to the ocean is unknown. 

#### Length Frequency Table and Figures

#### Figure 5. Length Frequency of all CCT
```{r 6. Length Frequency - CT Length Frequency All Years Combined, fig.cap = "Figure 5. Length Frequency of all CCT.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 8, fig.height = 6}

print(LF.plot_spring.all.CT)
```


#### Figure 6. Length frequency of Coastal CCT across years.
```{r 6. Length Frequency - CT Length Frequency Across Years, fig.cap = "Figure 6. Length Frequency of CCT across years.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 12, fig.height = 20}

print(LF.plot_spring.CT)
```

#### Figure 7. Length frequency of all Coho Salmon.
```{r 6. Length Frequency - CO Length Frequency All Years Combined, fig.cap = "Figure 7. Length Frequency of All Coho Salmon.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 8, fig.height = 6}

print(LF.plot_spring.all.CO)
```

#### Figure 8. Length frequency of Coho Salmon across years.
```{r 6. Length Frequency - CO Length Frequency Across Years, fig.cap = "Figure 8. Length Frequency of Coho Salmon across years.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 12, fig.height = 20}

print(LF.plot_spring.CO)
```

### 2.5 Age Composition
```{r 10. AgeClasses - Load Data, echo=FALSE, warning=FALSE, message = FALSE, include = FALSE}
source("SourceFiles/10. AgeClasses.R")
```

No scale data has been collected during juvenile enumeration work on Simms Creek. However, information collected on systems within the region suggests we can loosely apply the following age classes to juvenile CT and CO:

  -  CT < 80  ~ Age-0 
  -  CT < 120 ~ Age-1
  -  CT < 200 ~ Age-2
  -  CT > 200 ~ Age-2+
  -  CO < 80  ~ Age-0
  -  CO < 120 ~ Age-1
  -  CO > 120 ~ Age-1+ 

Applying these age bins to the length frequency data suggests that CCT are range in age from Age-1 to Age 3+, but are primarily Age-2 (Figure 9), while CO are almost exclusively Age-1 (Figure 10). Interestingly, Age-0 CO were present in 2009 and 2024, but not other years. While this may be coincidental, it's worth noting that the peak juvenile CCT counts were recorded in 2008 and 2024. There are a number of mechanisms that may explain why Age-0 CO were first observed in 2024: 1) they weren't recorded in past years, CO emigrated out of Simms Creek earlier than normal due to high CT abundance.

#### Figure 9. Age composition across years.
```{r 10. Age Class - CT Age Class Composition across years, fig.cap = "Figure 9. Assumed age class composition of juvenile CCT and Coho Salmon out migrating from Simms Creek since 2008.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 12, fig.height = 20}

juv.AgeClass.plot

```


#### Figure 10. Size by age class across years.
```{r 10. Age Class - Age Class Size across years, fig.cap = "Figure 10. Median size by age class of fish outmigrating from Simms Creek since 2008.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 12, fig.height = 20}

age.class.size

```

### 2.6. Migration Timing {.tabset .tabset-dropdown}
```{r 5. Capture Timing - Load Data, echo=FALSE, warning=FALSE, message = FALSE, include = FALSE}
 source("SourceFiles/5. Capture Timing.R")
```

```{r 5. Capture Timing - Prepare spring text values, echo=FALSE, warning=FALSE, message = FALSE, include = FALSE }

## Spring data for text
CT.first.detection.earliest <- format(min(pass.period.spring$minPass.min[pass.period.spring$Species=="CT"]), "%B %d")
CT.first.detection.latest   <- format(max(pass.period.spring$minPass.min[pass.period.spring$Species=="CT"]), "%B %d")
CT.first.detection.mean     <- format(mean(pass.period.spring$minPass.min[pass.period.spring$Species=="CT"], na.rm = TRUE), "%B %d")
CT.first.detection.SD       <- round(sd(pass.period.spring$minMeanDiff[pass.period.spring$Species=="CT"], na.rm = TRUE), 1)
CT.50p.mean                 <- format(mean(catch50prop.spring$meanDate50p[catch50prop.spring$Species=="CT"], na.rm = TRUE), "%B %d")
CT.50p.SD                   <- round(sd(catch50prop.spring$Date50pDiff[catch50prop.spring$Species=="CT"], na.rm = TRUE), 1)
CT.peak.mean                <- format(mean(catch_peak.spring$date.std_CT,na.rm = TRUE), "%B %d")
CT.peak.SD                  <- round(sd(catch_peak.spring$MeanDiff_CT,na.rm = TRUE),1)


CO.first.detection.earliest <- format(min(pass.period.spring$minPass.min[pass.period.spring$Species=="CO"]), "%B %d")
CO.first.detection.latest   <- format(max(pass.period.spring$minPass.min[pass.period.spring$Species=="CO"]), "%B %d")
CO.first.detection.mean     <- format(mean(pass.period.spring$minPass.min[pass.period.spring$Species=="CO"], na.rm = TRUE), "%B %d")
CO.first.detection.SD       <- round(sd(pass.period.spring$minMeanDiff[pass.period.spring$Species=="CO"], na.rm = TRUE), 1)
CO.50p.mean                 <- format(mean(catch50prop.spring$meanDate50p[catch50prop.spring$Species=="CO"], na.rm = TRUE), "%B %d")
CO.50p.SD                   <- round(sd(catch50prop.spring$Date50pDiff[catch50prop.spring$Species=="CO"], na.rm = TRUE), 1)
CO.peak.mean                <- format(mean(catch_peak.spring$date.std_CO,na.rm = TRUE), "%B %d")
CO.peak.SD                  <- round(sd(catch_peak.spring$MeanDiff_CO,na.rm = TRUE),1)

```

**2.4.1 Spring Outmigration**

Outmigrating juvenile CCT and Coho Salmon were first encountered at the trap over a similar period, from `r CT.first.detection.earliest` to `r CT.first.detection.latest` (mean $\pm$ SD = `r CT.first.detection.mean` $\pm$ `r CT.first.detection.SD` days) for CCT and `r CO.first.detection.earliest` to `r CO.first.detection.latest` for Coho (mean $\pm$ SD = `r CO.first.detection.mean` $\pm$ `r CO.first.detection.SD` days). On average 50% of all CCT had passed the fence by `r CT.50p.mean`$\pm$ `r CT.50p.SD` days while half of Coho Salmon migrants had passed the fence by `r CO.50p.mean`$\pm$ `r CO.50p.SD` days. Despite similarities in when migrations started and the timing that most migrants had past the fence, there was a noticeable difference in the timing of peak migrations (the date when the greatest number of fish passed the fence). For Coastal CCT, the overall mean $\pm$ SD peak migration occurred on `r CT.peak.mean`($\pm$ `r CT.peak.SD` days) (Figure 5) whereas overall mean peak Coho Salmon migration occurred more than a week later on `r CO.peak.mean` ($\pm$ `r CO.peak.SD` days) (Figure 6). Total number of daily captures of CCT and Coho Salmon per year are presented in Figure 6 and Figure 7, respectively. 

```{r 5. Capture Timing - Prepare fall text values, echo=FALSE, warning=FALSE, message = FALSE, include = FALSE }
## Fall data for text
CT.first.detection.earliest <- format(min(pass.period.fall$minPass.min[pass.period.fall$Species=="CT"]), "%B %d")
CT.first.detection.latest   <- format(max(pass.period.fall$minPass.min[pass.period.fall$Species=="CT"]), "%B %d")
CT.first.detection.mean     <- format(mean(pass.period.fall$minPass.min[pass.period.fall$Species=="CT"], na.rm = TRUE), "%B %d")
CT.first.detection.SD       <- round(sd(pass.period.fall$minMeanDiff[pass.period.fall$Species=="CT"], na.rm = TRUE), 1)
CT.50p.mean                 <- format(mean(catch50prop.fall$meanDate50p[catch50prop.fall$Species=="CT"], na.rm = TRUE), "%B %d")
CT.50p.SD                   <- round(sd(catch50prop.fall$Date50pDiff[catch50prop.fall$Species=="CT"], na.rm = TRUE), 1)
CT.peak.mean                <- format(mean(catch_peak.fall$date.std_CT,na.rm = TRUE), "%B %d")
CT.peak.SD                  <- round(sd(catch_peak.fall$MeanDiff_CT,na.rm = TRUE),1)


CO.first.detection.earliest <- format(min(pass.period.fall$minPass.min[pass.period.fall$Species=="CO"]), "%B %d")
CO.first.detection.latest   <- format(max(pass.period.fall$minPass.min[pass.period.fall$Species=="CO"]), "%B %d")
CO.first.detection.mean     <- format(mean(pass.period.fall$minPass.min[pass.period.fall$Species=="CO"], na.rm = TRUE), "%B %d")
CO.first.detection.SD       <- round(sd(pass.period.fall$minMeanDiff[pass.period.fall$Species=="CO"], na.rm = TRUE), 1)
CO.50p.mean                 <- format(mean(catch50prop.fall$meanDate50p[catch50prop.fall$Species=="CO"], na.rm = TRUE), "%B %d")
CO.50p.SD                   <- round(sd(catch50prop.fall$Date50pDiff[catch50prop.fall$Species=="CO"], na.rm = TRUE), 1)
CO.peak.mean                <- format(mean(catch_peak.fall$date.std_CO,na.rm = TRUE), "%B %d")
CO.peak.SD                  <- round(sd(catch_peak.fall$MeanDiff_CO,na.rm = TRUE),1)

```

**2.4.2 Fall Return Timing**

Adult Coho Salmon have been detected at the fence as early as `r CO.first.detection.earliest` and as late as `r CO.first.detection.latest`, though most of the run (50%) arrive within a week of `r CO.50p.mean` (Figure 14 to 19). Relative to spring sampling, CCT are encountered less frequently in the fall and  arrival timing appears to be considerably more variable (Figure 20 to 22).     


#### Spring and Fall Migration Timing Tables and Figures

#### Figure 11. Spring - Overall Capture Timing
```{r 5. Capture Timing - Spring - Overall Median Capture Timing, fig.cap = "Figure 11. Overall median spring capture timing.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 10, fig.height = 6}
Spring.Boxplot.Facet
```


#### Figure 12. Spring - Daily captures of CCT per year
```{r 5. Capture Timing - Spring - Daily CT Captures per year, fig.cap = "Figure 12. Total daily capture of CCT and proportion of total annual captures.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 10, fig.height = 25}

print(daily_catch_plot.Spring.CT)
```

#### Figure 13. Spring - Total daily captures of Coho Salmon per year
```{r 5. Capture Timing - Spring - Daily CO Captures per year, fig.cap = "Figure 13. Number of Coho Salmon captured during each day of spring fence operation since 2008.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 10, fig.height = 25}

print(daily_catch_plot.Spring.CO)
```

#### Figure 14. Fall - Total daily captures of Coho Salmon per year
```{r 5. Capture Timing - Fall - Daily CO Captures per year, fig.cap = "Figure 14. Number of Coho Salmon captured during each day of fall fence operation since 2008.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 10, fig.height = 25}

print(daily_catch_plot.Fall.CO)
```

#### Figure 15. Fall - Daily captures of CCT per year
```{r 5. Capture Timing - Fall - Daily CT Captures per year, fig.cap = "Figure 15. Total daily capture of CCT and proportion of total annual captures.", fig.topcaption = TRUE, echo=FALSE, warning=FALSE, message = FALSE, fig.width = 10, fig.height = 25}

print(daily_catch_plot.Fall.CT)
```




## 2.6 What are these fish doing???
```{r 8. Spring Spawners - Load Data, echo=FALSE, warning=FALSE, message = FALSE, include = FALSE}
 source("SourceFiles/8. SpringSpawners.R")
```

CCT show incredible diversity in the timing of their life history behaviours. Throughout their range, spawning has been documented in nearly every month of the year. In Puget Sound for instance, spawning has been reported from November through March and timing is highly variable between years ([Losee et al. 2016](https://afspubs.onlinelibrary.wiley.com/doi/abs/10.1080/02755947.2015.1129001#:~:text=These%20types%20of%20data%20have%20suggested%20a,coastal%20stream%20of%20southern%20Puget%20Sound%2C%20Washington.)). The spawn timing of CCT in Simms Creek is unknown, or at least undocumented, however, I would assume it occurs during a similar period to Puget Sound and is equally variable. 

The current dataset does provide some insight on spawn timing. Presumably, spawners will be >150 mm in length.

# FINISH WRITING THIS SECTION


## 3. Survival
### 3.1 What may be driving juvenile abundance
```{ 9. Survival, echo = FALSE, warning = FALSE, message = FALSE, include = FALSE}
source("SourceFiles/9. Survival.R")
```

To estimate the number of Coho Salmon that survive from egg to fry, we need to make a number of assumptions:

    - All adult Coho Salmon that enter Simms Creek and all juvenile Coho Salmon that outmigrate from Simms Creek are enumerated.  
    - All adult Coho Salmon that pass the fence will successfully spawn.
    - The sex ratio of adults is equal (50% are female, excluding jacks which are assumed male).
    - Each female will deposit ~2,600 eggs.

Importantly, we also need to consider the proportion of juveniles from each age-class the emigrate each year (and assume juvenile age assignments are accurate). Fish that outmigrate as Age-0 fry will be progeny of fish that spawned the previous fall, while fish that emigrate at Age-1 would have spent a full year in the stream (i.e., spawned 2 falls previous) and Age-1+ fish would have spawned 3 years previous. Using this information, we can then calculate the total number of juveniles produced by each spawning event to calculate egg-to-fry survival.



### 3.2 What about marine survival (from smolt to spawn)

Additional assumptions are required to estimate the number of juveniles that survive to return as adults:

    - Adults spend ~18-20 months at sea (1 winter), regardless of whether they leave Simms Creek as Age-0 or Age-1.
    - Jacks return to Simms Creek after ~6-8 months at sea (0 winters). 
    - All Coho Salmon that are enumerate at the fence originated from Simms Creek (i.e., there are no hatchery fish or strays from neighbouring streams).
    



##--------------------------

```{r exit}
knitr::knit_exit()
```

##--------------------------

```{r CCT - cum.Catch.plot,echo=FALSE, warning=FALSE, message = FALSE, fig.width = 9, fig.height = 15}

labels <- data.frame(Year = unique(Spring.Catch$Year), YYYEAR = unique(Spring.Catch$Year)) %>%
          # data.frame(Year = unique(CCT_catch$Year), YYYEAR = unique(CCT_catch$Year)) %>%
          mutate(YYYEAR = ifelse(Year == 2020, "2020 - COVID",
                                 ifelse(Year == 2021,"2021 - COVID",
                                        ifelse(Year == 2023, "2023 - Strike",Year))),
                 labX = as.Date(ifelse(Year == 2020, as.Date("2024-05-25"),
                                 ifelse(Year == 2021,as.Date("2024-05-25"),
                                        ifelse(Year == 2023, as.Date("2024-05-25"),as.Date("2024-04-16"))))))
ggplot(Spring.Catch) + 
      geom_col(aes(x= date.std, y =catch))+
      geom_line(aes(x= date.std, y = prop.scaled)) +
      geom_label(data = labels, aes(label = YYYEAR),
                x = as.Date("2024-04-15"), y = 205,
                hjust = "left", vjust = 0,
                inherit.aes = FALSE)+
      scale_x_date(date_breaks = "2 week", date_labels = "%b-%d") +
      scale_y_continuous("Total Captures (# of Fish)",
                         sec.axis = sec_axis(~./300, 
                         name = "Proportion of Total Catch (%)"))+
      facet_grid(Year~Species) +
      labs(x="", y = "Total Captures (# of Fish)") +
      theme_bw() +
      theme(strip.text.y = element_blank())
    
```

```{r CCT - cum.Catch.plot2,echo=FALSE, warning=FALSE, message = FALSE }
    ggplot(CCT_catch) +
        geom_line(aes(x= date.std, y = prop, color = Year)) +
        labs(x = "", y = "Proportion of Total Catch (%)") +
        scale_x_date(date_breaks = "1 week", 
                     minor_breaks = "1 day",
                     date_labels = '%b-%d')+ 
        facet_grid(Decade~.)+
        theme_bw() +
        theme(legend.position = "bottom")



```

```{r CT Catch Summary, echo=FALSE, warning=FALSE, message = FALSE}
### Prep Data ----
CT_catch <- catch_summary %>%
            select(1:13) %>%  # Select CT Data
            pivot_wider(names_from = Period, values_from = 3:13) %>%
            select(1, ends_with("Spring"), ends_with("Fall")) %>%
            ungroup() %>%
            add_row(Year = c(2020, 2021, 2023)) %>%
            arrange(Year)


## CT Kable ----
kable(CT_catch,
      "html",
      booktabs = T,
      align = c("c"),
      col.names = c("Year","Start", "End", "# Days Sampled",  
                    "n","Med.","Min","Max", "Mean", "SD" ,"Min","Max",
                    "Start", "End", "# Days Sampled",  
                    "n","Med.","Min","Max", "Mean", "SD" ,"Min","Max"),
      caption = "**Table 1. Spring and Fall Trapping of CCT.**",
      digits = 1) %>%
  #column_spec(c(1, 3,10,17), bold = TRUE) %>%
  kable_styling("striped", full_width =  FALSE,
                position = "center", 
                font_size = 12,
                fixed_thead = TRUE) %>%
  add_header_above(c(" "=1, "Sample Period" = 3, "Capture Timing" = 4,"Fork Length (mm)" = 4,
                     "Sample Period" = 3, "Capture Timing" = 4,"Fork Length (mm)" = 4)) %>%
  add_header_above(c(" " = 1,"Spring" = 11, "Fall" = 11)) 
 
```

```{r CT Size Distribution, length-frequency all years,echo=FALSE, warning=FALSE, message = FALSE}
## Length-Frequency Plot of all CCT captured to date.
    ## Prepare Data
    CT_dat <- data_all %>% 
                    filter(Species == "CT") %>%
                    mutate(date.std =  case_when(year(Date) >= 0 ~ 'year<-'(Date, 2024))) 
                    

      ## Prepare Plot
      all_years.plot <- ggplot(CT_dat) +
                            geom_histogram(aes(x = Length), binwidth = 5, color = "black", fill = "white") + 
                            labs(x = "Fork Lenght (mm)", y = "Frequency (# Fish)") +
                            scale_x_continuous(breaks = seq(50, 450, by = 25))+
                            #scale_y_continuous(breaks = seq(0, 450, 50))+
                            theme(axis.text.x = element_text(angle = 45, vjust = 1.2, hjust = 1)) +
                            theme_bw() +
                            facet_grid(Year~.)
```

```{r compare regional trends, echo=FALSE, warning=FALSE, message = FALSE}
## Prep Regional Abundance Dataset
reg.abund <- reg.dat %>% 
                mutate(data_set = "DFO") %>%
                select(data_set, year, species, spawners, smoothedSpawners) %>%
                rename(Year     = year,
                       Species  = species,
                       n        = spawners,
                       n_smooth = smoothedSpawners) %>% 
                mutate(Species = recode(as.factor(Species),
                                                 "Coho"      = "CO_Adult",
                                                 "Chinook"   = "CN",
                                                 "Pink"      = "PK",
                                                 "Chum"      = "CM",
                                                 "Sockeye"   = "SK",
                                                 "Steelhead" = "ST"),
                                Species = factor(Species, 
                                                 levels = c("CT","CO_Adult", "CN","CM","PK", "SK", "ST")))
# Prepare Simms Data and Join with Regional Data                
catch_spring <- data_all %>%
                    filter(Period == "Spring",
                           Species %in% c("CT", "CO")) %>%
                    group_by(Year,Species) %>%
                    summarise(n = n()) %>%
                    filter(!is.na(Species)) %>%
                    mutate(n_smooth = 0,
                           data_set = "Simms") %>% 
                    relocate(data_set) %>%
                rbind(reg.abund)

catch_spring_CO <- catch_spring %>%
                      filter(Year >= 2008) %>%
                      select(!n_smooth)

ggplot(catch_spring_CO, 
       aes(x = Year, y = n)) +
  geom_point() + 
  geom_line() + 
  facet_grid(Species ~., scales = "free")

catch_spring_long <- catch_spring_CO %>%
      select(!data_set) %>%
      pivot_wider(names_from = Species, values_from = n) %>%
      drop_na()

cor(catch_spring_long)
```

# 3. Fall Fence Operation
### 3.1. Monitoring Effort



